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請用此 Handle URI 來引用此文件: http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/53669
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dc.contributor.advisor林逸彬(Yi-Pin Lin)
dc.contributor.authorYi-Chen Linen
dc.contributor.author林倚楨zh_TW
dc.date.accessioned2021-06-16T02:27:17Z-
dc.date.available2020-08-06
dc.date.copyright2015-08-06
dc.date.issued2015
dc.date.submitted2015-08-04
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Hoigné, J., Bader, H. (1983). Rate constants of reactions of ozone with organic and inorganic compounds in water—II: dissociating organic compounds. Water research, 17(2), 185-194.
Hoigné, J., Bader, H., Haag, W. R., Staehelin. (1985). Rate constants of reactions of ozone with organic and inorganic compounds in water—II: Inorganic compounds and radicals. Water research, 19, 993-1004.
Huber, M. M., Canonica, S., Park, G. Y., von Gunten, U. (2003). Oxidation of pharmaceuticals during ozonation and advanced oxidation processes. Environmental Science and Technology, 37(5), 1016-1024.
Kolpin, D. W., Furlong, E. T., Meyer, M. T., Thurman, E. M., Zaugg, S. D., Barber, L. B., Buxton, H. T. (2002) Pharmaceuticals, hormones, and other organic wastewater contaminants in US streams, 1999-2000: A national reconnaissance. Environmental Science and Technology, 36 (6), 1202-1211.
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Song, W., Cooper, W. J., Mezyk, S. P., Greaves, J., Peake, B. M. (2008). Free radical destruction of β-blockers in aqueous solution. Environmental Science and Technology, 42(4), 1256-1261.
Sonntag, C., von Gunten, U. (2012). Chemistry of ozone in water and wastewater treatment: From basic principles to applications. IWA publishing.
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von Gunten, U. (2003). Ozonation of drinking water: Part I. Oxidation kinetics and product formation. Water research, 37(7), 1443-1467.
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Yong, E. L., Lin, Y. P. (2012). Incorporation of initiation, promotion and inhibition in the R ct concept and its application in determining the initiation and inhibition capacities of natural water in ozonation. Water research, 46(6), 1990-1998.
Yong, E. L., Lin, Y. P. (2013). Kinetics of natural organic matter as the initiator, promoter, and inhibitor, and their influences on the removal of ibuprofen in ozonation. Ozone: Science and Engineering, 35(6), 472-481.
dc.identifier.urihttp://tdr.lib.ntu.edu.tw/jspui/handle/123456789/53669-
dc.description.abstract臭氧被廣泛應用於去除自來水和廢水中的有機污染物,近幾年來更是運用於降解地表水及地下水中之新興污染物。由於天然有機物(NOM)與臭氧及氫氧自由基的反應相當複雜,所以天然有機物在臭氧處理程序中之影響尚未被闡明。故本研究的目的為:(1)測定天然有機物於臭氧處理程序中起始反應(initiation)、促進反應(promotion)、抑制反應(inhibition)以及與臭氧直接反應之速率常數。(2) 探討pH值及溫度對起始反應、促進反應、抑制反應以及與臭氧直接反應速率常數之影響。(3) 測定及模擬天然有機物於臭氧處理程序中對新興污染物去除之影響。本研究所使用之四種自然水體為:新店溪(新北市)、宜蘭河(宜蘭市)、金沙水庫(金門縣)及台中地下水(台中縣)。結果顯示起始反應、抑制反應及與臭氧的直接反應之速率常數會隨著pH值升高而增加,但促進反應之速率常數則明顯的趨勢。在溫度影響的部分,所有的速率常數皆是隨著溫度的升高而增加。在天然有機物於臭氧處理程序下對新興污染物降解影響的部分,從結果顯示都可利用所測得之速率常數得到良好的預測結果。zh_TW
dc.description.abstractOzonation has been widely used for removing organic contaminants in water treatment. The effect of natural organic matter (NOM) on this process, however, is not well understood due to the complex reactions of NOM with ozone and •OH generated from ozone decomposition. The objectives of this study are to determine the rate constants of NOM from different sources in terms of initiation, promotion, inhibition and direct ozone reactions in the ozonation process and to investigate the influences of NOM on the removal of emerging contaminants. The rate constants of NOM in four natural waters including Hsintien river (New Taipei City), Yilan river (Yilan City), Jinsha reservoir (Kinmen County) and Taichung groundwater (Taichung County) were determined using a recently developed approach that integrates the pseudo first order ozone decomposition kinetics, transient steady state •OH concentration and the Rct concept. The effects of pH value and temperature on the rate constants were also determined. With these rate constants, the influences of NOM on the degradation of three emerging contaminants including ibuprofen, acetylsulfamethoxazole and metoprolol can be fairly well predicted.en
dc.description.provenanceMade available in DSpace on 2021-06-16T02:27:17Z (GMT). No. of bitstreams: 1
ntu-104-R02541213-1.pdf: 1195141 bytes, checksum: e8b1405af142e5abb060ecda57547908 (MD5)
Previous issue date: 2015
en
dc.description.tableofcontentsTABLE OF CONTENT
摘要 i
SUMMARY ii
TABLE OF CONTENT iii
LIST OF FIGURES v
LIST OF TABLES vi
ABBREVIATIONS vii
Chapter 1 INTRODUCTION 1
1.1. Research background 1
1.2. Objectives 2
Chapter 2 LITERATURE REVIEW 4
2.1. Basic properties of ozone 4
2.2. Ozonation of organic compounds 5
2.3. The Rct concept and modified Rct model 8
2.4. Ozonation of emerging contaminants 12
CHAPTER 3 MATERIALS AND METHODS 15
3.1. Chemicals 15
3.2. Stock Solutions 15
3.3. Natural waters 16
3.4. Ozonation experiments 17
3.5. Analytical method 18
Chapter 4 RESULTS AND DISCUSSION 21
4.1. Determination of the initiation, promotion, inhibition and direct ozone reaction rate constants of NOM in surface water and groundwater 21
4.2. Effect of pH value on NOM rate constants 30
4.3. Effect of temperature on NOM rate constants 31
4.4. Quantify and model the effects of NOM on the degradation of ibuprofen, acetylsulfamethoxazole and metoprolol 35
Chapter 5 CONCLUSIONS AND RECOMMENDATIONS 39
5.1. Conclusions 39
5.2. Recommendations for future study 40
REFERENCES 42
 
LIST OF FIGURES
Figure 1.1. Reactions of ozone with the presence of foreign compounds acting as the initiator, promoter and inhibitor 5
Figure 4.1. Ozone decomposition for natural waters in the presence of 0-0.3 mM tert-butanol 22
Figure 4.2. The Rct plots for natural waters in the presence of 0-0.3 mM tert-butanol 23
Figure 4.3. The plots of 1/Rct vs kSS[S] for four natural waters 27
Figure 4.4. The plots of kobs vs. Rct for four natural waters 28
Figure 4.5. The Arrhenius plot for different reaction modes of Yilan river NOM 34
Figure. 4.6 Effect of pH value on the degradation of ibuprofen, acetylsulfamethoxazole and metoprolol in Yilan river water 37
Figure. 4.7 Effect of temperature on the degradation of ibuprofen, acetylsulfamethoxazole and metoprolol in Yilan river water 38


LIST OF TABLES
Table 2.1 Physical properties of ozone 4
Table 3.1. Characteristics of natural waters used in this study 17
Table 4.1. The second stage Rct values determined for the four natural waters in the presence of 0-0.3 mM tert-butanol 24
Table 4.2. The second-order rate constants of initiation (kI), promotion (kP), inhibition (kS) and direct reaction (kD) for NOM in four natural waters 29
Table 4.3. The relative contributions of direction reaction (kD) vs. initiation (kI) in the reaction between ozone and NOM and the relative contributions of promotion (kP) vs. inhibition (kS) in the reaction between •OH and NOM for the four natural waters 29
Table. 4.4 The initiation (kI), promotion (kP), inhibition (kS) and direct reaction (kD) rate constants for Yilan river NOM at pH 6.0-8.0 31
Table 4.5. The initiation (kI), promotion (kP), inhibition (kS) and direct reaction (kD) rate constants for Yilan river NOM at 10-30 0C 33
Table. 4.6 The rate constants with •OH are similar and those with ozone differ substantially as show below water 35
dc.language.isoen
dc.subject天然有機物(NOM)zh_TW
dc.subject起始劑zh_TW
dc.subject臭氧zh_TW
dc.subject促進劑zh_TW
dc.subject抑制劑zh_TW
dc.subject活化能和新興污染物zh_TW
dc.subjectinitiatoren
dc.subjectactivation energy and emerging contaminantsen
dc.subjectpromoter and inhibitoren
dc.subjectNatural organic matter (NOM)en
dc.subjectozoneen
dc.title天然有機物於臭氧降解程序中氫氧自由基之生成與消耗及其去除新興污染物之影響zh_TW
dc.titleEffect of natural organic matter on the formation and consumption of OH radical and removal of emerging contaminants in ozonationen
dc.typeThesis
dc.date.schoolyear103-2
dc.description.degree碩士
dc.contributor.oralexamcommittee蔣本基(Pen-Chi Chiang),侯嘉洪(Chia-Hung Hou)
dc.subject.keyword臭氧,天然有機物(NOM),起始劑,促進劑,抑制劑,活化能和新興污染物,zh_TW
dc.subject.keywordozone,Natural organic matter (NOM),initiator,promoter and inhibitor,activation energy and emerging contaminants,en
dc.relation.page44
dc.rights.note有償授權
dc.date.accepted2015-08-04
dc.contributor.author-college工學院zh_TW
dc.contributor.author-dept環境工程學研究所zh_TW
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